chloroacetic acid

Monochloroacetic acid

79-11-8

2-chloroacetic acid

Chloracetic acid

Chloroethanoic acid

Acetic acid, chloro-

Acide chloracetique

Monochloroethanoic acid

Monochloracetic acid

Monochloorazijnzuur

Monochloressigsaeure

Acidomonocloroacetico

2-chloro-acetic acid

Acide monochloracetique

Chloroacetic acid, solid

Acide chloroacetique

Kyselina chloroctova

Acetocaustin

Chloroacetic

2-chloro-ethanoic acid

Caswell No. 179B

Chloroacetic acid [BSI:ISO]

Acetic acid, 2-chloro-

.alpha.-Chloroacetic acid

NSC 142

Monochloorazijnzuur [Dutch]

NCI-C60231

Acide chloracetique [French]

Kyselina chloroctova [Czech]

monochloro acetic acid

Monochloressigsaeure [German]

Acide chloroacetique [French]

alpha-Chloroacetic acid

Acidomonocloroacetico [Italian]

CCRIS 2117

HSDB 939

Acide monochloracetique [French]

Chloroacetic acid, molten

Monochloroacetic acid [BSI:ISO]

Acide chloracetique [ISO-French]

Chloroacetic acid (80% or less)

chloro-acetic acid

EINECS 201-178-4

Acetocaustin (TN)

EPA Pesticide Chemical Code 279400

UNII-5GD84Y125G

BRN 0605438

CH2ClCOOH

DTXSID4020901

CHEBI:27869

AI3-25035

NSC-142

5GD84Y125G

CHLOROACETIC-ACID

alpha-chloro-acetic acid

DTXCID20901

Monochloracetic acidacide monochloracetique

Chloroacetic acid, liquid

EC 201-178-4

4-02-00-00474 (Beilstein Handbook Reference)

MFCD00002683

CHLOROACETIC ACID CRYSTALLINE

Chloroacetic acid, molten [UN3250] [Poison]

Chloroacetic acid, solid [UN1751] [Poison]

Acide chloracetique (ISO-French)

MONOCHLOROACETIC ACID (MART.)

MONOCHLOROACETIC ACID [MART.]

sJPhLQDIKTp@

MCAA

UN1750

UN1751

UN3250

Chloressigsauer

Chlorethansauere

CHLOROACETIC ACID, ACS

cloroacetic acid

chloro acetic acid

Monochloor azijnzuur

R3W

ClCH2COOH

monochloro-acetic acid

Acidomono chloroacetico

Acide monochloroacetique

Chloroacetic acid, 99%

Chloroacetic acid, solid [UN1751] [Poison]

bmse000367

WLN: QV1G

Chloroacetic acid, molten [UN3250] [Poison]

Chloroacetic acid, >=99%

NCIOpen2_002217

Chloroacetic acid, ACS grade

MLS001065621

BIDD:ER0630

CHEMBL14090

CHLOROACETIC ACID [MI]

NSC142

CHLOROACETIC ACID [ISO]

Chloroacetic acid, solid (dot)

CHLOROACETIC ACID [HSDB]

CHLOROACETIC ACID [INCI]

FOCAUTSVDIKZOP-UHFFFAOYSA-

CHLOROACETIC ACID [VANDF]

BCP20585

NSC42970

STR00326

Tox21_201114

BBL037260

LMFA01090068

MONOCHLOROACETIC ACID [VANDF]

NSC-42970

STL197882

Chloroacetic acid, analytical standard

AKOS000118920

MONOCHLOROACETIC ACID [WHO-DD]

MCULE-9228754880

UN 1751

CAS-79-11-8

NCGC00091473-01

NCGC00091473-02

NCGC00091473-03

NCGC00258666-01

SMR000568484

Chloroacetic acid, for synthesis, 99.0%

Chloroacetic acid, ACS reagent, >=99.0%

Chloroacetic acid, purum, >=97.0% (T)

C2123

NS00003112

Chloroacetic acid, puriss., >=99.0% (T)

EN300-16767

C06755

D07677

Chloroacetic acid, JIS special grade, >=99.0%

Q409013

J-520023

Chloroacetic acid, PESTANAL(R), analytical standard

F2190-0289

InChI=1/C2H3ClO2/c3-1-2(4)5/h1H2,(H,4,5)

Chloroacetic acid 1000 microg/mL in Methyl-tert-butyl ether

A pKa of 2.87(1) indicates chloroacetic acid will exist almost entirely in the anion form at pH values of 5 to 9 and, therefore, volatilization from water or moist soil surfaces is not expected to be an important fate process(SRC). Chloroacetic acid is not expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 6.5X10-2 mm Hg(3).

The Koc of chloroacetic acid is estimated as 2(SRC), using a log Kow of 0.22(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that chloroacetic acid is expected to have very high mobility in soil. The pKa of chloroacetic acid is 2.87(4), indicating that this compound will exist almost entirely in the anion form in the environment and anions generally do not adsorb more strongly to soils containing organic carbon and clay than their neutral counterparts(5).

4-(2-Aminoethyl)benzenesulfonyl fluoride

34284-75-8

AEBSF

4-(2-Aminoethyl)benzenesulfonylfluoride

4-(2-aminoethyl)benzene-1-sulfonyl fluoride

Benzenesulfonyl fluoride, 4-(2-aminoethyl)-

F5D36L5354

AES

4-beta-Aminoethylbenzolsulfofluoride

CHEMBL1256178

SR-01000075690

ABSF

Lopac-A-8456

Lopac0_000132

SCHEMBL77781

CHEMBL1096339

UNII-F5D36L5354

DTXSID40187844

BDBM50398077

CCG-204227

DB07347

SDCCGSBI-0050120.P002

NCGC00015097-01

NCGC00015097-02

NCGC00015097-03

NCGC00015097-12

NCGC00162071-01

PD005322

NS00015316

[4-(2-Aminoethyl)-benzenesulphonyl fluoride]

G22633

EN300-1581783

Q290992

BENZENESULFONYL FLUORIDE, P-(2-AMINOETHYL)-

SR-01000075690-6

1,4-DICHLOROBENZENE

106-46-7

p-Dichlorobenzene

paradichlorobenzene

para-Dichlorobenzene

Paracide

Paramoth

Dichlorobenzene

Paranuggets

Santochlor

Paradow

Benzene, 1,4-dichloro-

Evola

Persia-perazol

p-Dichlorobenzol

p-Chlorophenyl chloride

Globol

Paradi

p-Dichlorbenzol

Para crystals

Dichlorocide

Di-chloricide

Paradichlorbenzol

PDCB

p-Diclorobenzene

1,4-Dichloorbenzeen

p-Dichloorbenzeen

Paradichlorobenzol

1,4-Dichlor-benzol

dichloricide

1,4-Diclorobenzene

Benzene, p-dichloro-

1,4-dichloro-benzene

Parazene

RCRA waste number U070

RCRA waste number U071

RCRA waste number U072

Para-zene

Dichlorobenzene, p-

NCI-C54955

Kaydox

p-Dichlorbenzene

PDB

NSC 36935

Dichlorobenzene, para

D149TYB5MK

1,3-Cyclohexadien-5-yne,1,4-dichloro-

CHEMBL190982

DTXSID1020431

CHEBI:28618

MFCD00000604

NSC-36935

NCGC00094540-01

4-Dichlorobenzene

DTXCID30431

p-DCB

Caswell No. 632

p-Dichlorbenzol [German]

p-Dichloorbenzeen [Dutch]

Paradichlorbenzol [German]

p-Diclorobenzene [Italian]

1,4-chlorobenzene

68890-93-7

CAS-106-46-7

CCRIS 307

1,4-Dichloorbenzeen [Dutch]

1,4 dichlorobenzene

1,4-Dichlor-benzol [German]

1,4-Diclorobenzene [Italian]

HSDB 523

EINECS 203-400-5

RCRA waste no. D027

RCRA waste no. U072

UNII-D149TYB5MK

EPA Pesticide Chemical Code 061501

diclorobenzene

AI3-0050

p-dichlorobenzen

AI3-00050

p-dichloro-benzene

Benzene,4-dichloro-

Dichlorobenzene, solid

1, 4-Dichlorobenzene

Spectrum_001891

SpecPlus_000512

Benzene, 1,4-dichloro-, radical ion(1-)

Spectrum2_001869

Spectrum3_000846

Spectrum4_000686

Spectrum5_002008

p-Dichlorbenzol(GERMAN)

p-Dichloorbenzeen(DUTCH)

Para-Dichlorobenzene,(S)

WLN: GR DG

EC 203-400-5

p-Diclorobenzene(ITALIAN)

Dichlorobenzene, p-, solid

SCHEMBL5191

BSPBio_002431

KBioGR_001151

KBioSS_002421

SPECTRUM330055

BIDD:ER0278

DivK1c_006608

SPBio_001718

P-DICHLOROBENZENE [MI]

1, 4-Dichloorbenzeen(DUTCH)

1,4-Dichlor-benzol(GERMAN)

1,4-Diclorobenzene(ITALIAN)

1,4-Dichlorobenzene, >=99%

KBio1_001552

KBio2_002415

KBio2_004983

KBio2_007551

KBio3_001931

PARADICHLOROBENZENE [VANDF]

PARADICHLOROBENZENE [MART.]

AMY40774

HY-Y0496

NSC36935

1,4-DICHLOROBENZENE [HSDB]

PARADICHLOROBENZENE [WHO-DD]

Tox21_111293

Tox21_200399

Tox21_300018

1,4-Dichlorobenzene-UL-14C, neat

BDBM50159263

c0593

CCG-39407

s6300

STL445582

AKOS000120016

MCULE-2384194593

UN 1592

1,4-Dichlorobenzene (ACD/Name 4.0)

NCGC00094540-02

NCGC00094540-03

NCGC00094540-04

NCGC00094540-05

NCGC00253934-01

NCGC00257953-01

55232-43-4

Benzene,1-chloro-4-(chloro-38cl)-(9ci)

CS-0015284

D0687

NS00010822

S0666

EN300-19990

1,4-Dichlorobenzene 10 microg/mL in Isooctane

106-46-7; 25321-22-6(mixedisomers)

C07092

G75779

1,4-Dichlorobenzene 100 microg/mL in Methanol

1,4-Dichlorobenzene 1000 microg/mL in Methanol

1,4-Dichlorobenzene, SAJ first grade, >=99.0%

Q161529

J-503986

1,4-Dichlorobenzene, PESTANAL(R), analytical standard

F0001-0123

Z104476304

InChI=1/C6H4Cl2/c7-5-1-2-6(8)4-3-5/h1-4

The Henry's Law constant for 1,4-dichlorobenzene is 2.41X10-3 atm-cu m/mole at 20 °C(1). This value indicates that 1,4-dichlorobenzene will volatilize from water(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as approximately 4 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as approximately 5 days(SRC). 1,4-Dichlorobenzene's Henry's Law constant(1) indicates that volatilization from moist soil surfaces is expected. 1,4-Dichlorobenzene is expected to volatilize from dry soil surfaces based on a vapor pressure of 1.74 mm Hg at 25 °C(3).

An experimental Koc value of 273(1) was determined for 1,4-dichlorobenzene in silt loam soil and a value of 390 was reported in Lincoln fine sand(2). According to a recommended classification scheme(3), these Koc values suggest that 1,4-dichlorobenzene has moderate mobility in soil(SRC). A log Koc value of 4.8 was measured for 1,4-dichlorobenzene from sediment of Lake Ketelmeer, Netherlands(4).

2,4-DICHLOROBENZOIC ACID

50-84-0

Benzoic acid, 2,4-dichloro-

DTXSID0024977

CHEBI:30748

NSC-578

MFCD00002414

2,4-Dichlorobenzoicacid

0SR0320D45

NSC 578

2,4 dichlorobenzoic acid

EINECS 200-067-8

2,4-Dichloro-benzoic acid

BRN 1868192

AI3-14873

CCRIS 9472

UNII-0SR0320D45

2,4-Dichlorobenzoic Acid; Furosemide Imp. E (EP); 2,4-Dichlorobenzyl Alcohol Impurity E; Furosemide Impurity E

2,4-Dichlorbenzoic acid

WLN: QVR BG DG

bmse000672

C06670

SCHEMBL111279

DTXCID104977

NSC578

CHEMBL1492029

2,4-Dichlorobenzoic acid, 98%

STR01599

DICHLOROBENZOIC ACID, 2,4-

Tox21_200756

STK297837

AKOS000119754

CS-W013226

PS-4049

CAS-50-84-0

NCGC00091214-01

NCGC00091214-02

NCGC00091214-03

NCGC00258310-01

AC-22899

PD163264

SY007062

FUROSEMIDE IMPURITY E [EP IMPURITY]

AM20050123

D0337

NS00010527

EN300-18039

A23852

D77744

AB01333124-02

AG-617/02198062

W-105928

Q27104142

Z57127531

F2191-0069

2,4-Dichlorobenzoic acid, PESTANAL(R), analytical standard

InChI=1/C7H4Cl2O2/c8-4-1-2-5(7(10)11)6(9)3-4/h1-3H,(H,10,11

NA

NA

CHLOROFORM

Trichloromethane

67-66-3

Trichlormethan

Formyl trichloride

Trichloroform

Methane, trichloro-

Methenyl trichloride

Chloroforme

Methyl trichloride

Methane trichloride

CHCl3

R 20 (Refrigerant)

Triclorometano

Cloroformio

Trichloormethaan

Freon 20

1,1,1-Trichloromethane

Methenyl chloride

RCRA waste number U044

NCI-C02686

Chloroformum

Caswell No. 192

Chloroform bp

Methylidyne trichloride

HSDB 56

Refrigerant R20

CCRIS 137

NSC 77361

trichloro-methane

Hcc 20

R 20

EINECS 200-663-8

NSC-77361

EPA Pesticide Chemical Code 020701

UNII-7V31YC746X

BRN 1731042

DTXSID1020306

CHEBI:35255

AI3-24207

7V31YC746X

Chloroform [UN1888] [Poison]

chloroformium pro narcosi

DTXCID10306

EC 200-663-8

4-01-00-00042 (Beilstein Handbook Reference)

NSC77361

NCGC00090794-01

chloroform CHCl3

CHLOROFORM (II)

CHLOROFORM [II]

Chloroform, HPLC Grade

CHLOROFORM (IARC)

CHLOROFORM [IARC]

CHLOROFORM (MART.)

CHLOROFORM [MART.]

CHLOROFORM (USP-RS)

CHLOROFORM [USP-RS]

Chloroform, analytical standard

Chloroforme [French]

Cloroformio [Italian]

Trichlormethan [Czech]

Chloroform [NF XVII]

Trichloormethaan [Dutch]

Triclorometano [Italian]

MFCD00000826

CAS-67-66-3

Chloroform [NF]

CHLOROBUTANOL IMPURITY A (EP IMPURITY)

CHLOROBUTANOL IMPURITY A [EP IMPURITY]

CHLOROFORM, ACS

CHLOROFORMWith Amylene

CHLOROFORMWith Ethanol

UN1888

RCRA waste no. U044

chlorform

chloroforrn

cloroform

trichlormethane

chloro form

chloro-form

Chloroform-

Chloroform, for HPLC, >=99.8%, contains 0.5-1.0% ethanol as stabilizer

trichloro- methane

methane trichloride

tris(chloranyl)methane

CCl3H

HCCl3

Chloroform, for HPLC

Trichloromethane, 9CI

CHLOROFORM [MI]

Chloroform, ethanol-free

Trichlormethan/Chloroform

WLN: GYGG

CHLOROFORM [HSDB]

CHLOROFORM [INCI]

CHLOROFORM [VANDF]

CHLOROFORMUM [HPUS]

R 20(REFRIGERANT)

CHLOROFORM [WHO-DD]

Pesticide Code: 020701

CHEMBL44618

Chloroform, p.a., 99.8%

GTPL2503

NCI-CO2686

CHLOROFORM [GREEN BOOK]

DTXSID10953654

R 20 (VAN)

Chloroform with Amylene HPLC grade

Chloroform, Spectrophotometric Grade

Chloroform (stabilized with ethanol)

Tox21_111024

Tox21_202494

Chloroform, for HPLC, >=99.5%

Chloroform, for HPLC, >=99.8%

AKOS000269026

Chloroform 100 microg/mL in Methanol

DB11387

InChI=1/CHCl3/c2-1(3)4/h1

MCULE-5607930311

UN 1888

Chloroform 5000 microg/mL in Methanol

Chloroform, purification grade, >=99%

NCGC00090794-02

NCGC00260043-01

F 20

R-20

Chloroform (Stabilized with ~1% Ethanol)

Trichloromethane 10 microg/mL in Methanol

Chloroform, JIS special grade, >=99.0%

Trichloromethane 100 microg/mL in Methanol

C0819

NS00007346

Trichloromethane 5000 microg/mL in Methanol

Chloroform, HPLC grade stabilized with ethanol

Chloroform (stabilized with 2-Methyl-2-butene)

Chloroform, SAJ super special grade, >=99.0%

A835850

L023971

Q172275

BRD-K88785477-001-01-8

Chloroform (Anhydrous) Contains Amylenes as stabilizer

Chloroform, for HPLC, >=99.8%, amylene stabilized

Chloroform, 99.8%, ACS Reagent stabilized with Ethanol

Chloroform, technical, amylene stabilized, >=99% (GC)

F0001-1775

Chloroform, technical grade, 95%, contains 50 ppm Amylene

Chloroform, anhydrous, contains amylenes as stabilizer, >=99%

Chloroform, for HPLC, >=99.8% (chloroform + ethanol, GC)

Chloroform stabilized with 50-200 ppm Amylene ACS Reagent Grade

Chloroform, >=99%, PCR Reagent, contains amylenes as stabilizer

Chloroform, ACS reagent, >=99.8%, contains amylenes as stabilizer

Chloroform, AR, contains 1-2% ethanol as stabilizer, >=99.5%

Chloroform, AR, contains 100 ppm amylene as stabilizer, >=99.5%

Chloroform, contains 100-200 ppm amylenes as stabilizer, >=99.5%

Chloroform, contains amylenes as stabilizer, ACS reagent, >=99.8%

Chloroform, contains ethanol as stabilizer, ACS reagent, >=99.8%

Chloroform, LR, contains 100 ppm amylene as stabilizer, >=99%

Chloroform, p.a., ACS reagent, 99.8%, contains 0.005% Amylene

Chloroform, SAJ first grade, >=99.0%, contains 0.4-0.8% ethanol

Chloroform, UV HPLC spectroscopic, 99.9%, contains 50 ppm Amylene

Chloroform, ACS reagent, Reag. Ph. Eur., contains ethanol as stabilizer

Chloroform, anhydrous, >=99%, contains 0.5-1.0% ethanol as stabilizer

Chloroform, Pharmaceutical Secondary Standard; Certified Reference Material

Chloroform, puriss. p.a., reag. ISO, reag. Ph. Eur., 99.0-99.4% (GC)

Chloroform, UV HPLC spectroscopic, 99.0%, contains 0.6-1.0% Ethanol

Chloroform, ACS reagent, >=99.8%, contains 0.5-1.0% ethanol as stabilizer

Chloroform, ACS spectrophotometric grade, >=99.8%, contains amylenes as stabilizer

Chloroform, biotech. grade, >=99.8%, contains 0.5-1.0% ethanol as stabilizer

Chloroform, p.a., ACS reagent, reag. ISO, 99.8%, contains 50 ppm Amylene

Chloroform, puriss. p.a., ACS reagent, >=99.8% (chloroform + ethanol, GC)

Chloroform, ReagentPlus(R), >=99.8%, contains 0.5-1.0% ethanol as stabilizer

Residual Solvent Class 2 - Chloroform, United States Pharmacopeia (USP) Reference Standard

Chloroform, ACS spectrophotometric grade, >=99.8%, contains 0.5-1.0% ethanol as stabilizer

Chloroform, contains ethanol as stabilizer, meets analytical specification of DAB9, BP, 99-99.4% (GC)

Residual Solvent - Chloroform, Pharmaceutical Secondary Standard; Certified Reference Material

The Henry's Law constant for chloroform is 3.67X10-3 atm-cu m/mole(1). This Henry's Law constant indicates that chloroform is expected to volatilize from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 3.5 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 4.4 days(SRC). Three laboratory studies of the evaporation of chloroform from water gave half-lives of 3-5.6 hrs with moderate mixing conditions(3-5). Chloroform volatilization constants were estimated in chilled (4 deg C) and boiled (100 deg C) water to be 0.88/hour and 1.50/hour, respectively(6). Estimated volatilization constants in experiments at 25 and 30 deg C ranged from 0.055/hour to 0.411/hour depending on the width and liquid level in the glass(6). Chloroform's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). Chloroform is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 197 mm Hg(7).
Literature: (1) Gossett JM; Environ Sci Tech 21: 202-6 (1987) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Smith JH et al; Environ Sci Technol 14: 190-6 (1980) (4) Rathbun RE, Tai DY; Water Res 15: 243-50 (1981) (5) Robert PV, Dandliker PG; Environ Sci Technol 17: 484-9 (1983) (6) Batterman S et al; Environ Sci Technol 34: 4418-24 (2000) (7) Boublik T et al; The Vapor Pressures of Pure Substances, Vol. 17; Amsterdam, Netherlands: Elsevier Sci (1984)

A soil sorption study was conducted on chloroform in three distinctly different soils(1). Soils used were from Missouri (composed of 11.4% sand, 52.7% silt, 33.4% clay, 2.4% organic matter, at pH 6.9), California (composed of 45.1% sand, 35.2% silt, 21.7% clay, organic matter 1.7%, at pH 8.1), and Florida (composed of 91.7% sand, 6.3% silt, 2.0% clay, 1.6% organic matter, at pH 4.7)(1). The ratio of the amount of contaminant adsorbed in micrograms per gram of soil to the equilibrium concn in ppm was used to calculate a Kd value of 2.133 in the Missouri soil, 1.941 in the California soil, and 1.763 in the Florida soil(1). These values correspond to a Koc value ranging from 153-196 based upon the relationship between Kd and Koc(2). Chloroform is adsorbed most strongly to peat moss, less strongly to clay, very slightly to dolomite limestone and not at all to sand(3). The Koc values measured for 2 soils was 34; 3 other soils with the lowest organic carbon content in the same study gave no appreciable adsorption(4). Field experiments in which chloroform was injected into an aquifer and the concn in a series of observation wells determined, demonstrated that chloroform is very poorly retained by aquifer material (retardation factor 2-4), less so than other C1- and C2-halogenated compounds studied(4-5). Laboratory percolation studies with a sandy soil gave similar results (retardation factor <1.5)(6). Chloroform was reported to have a Koc of 65(7), 55(8), 47(9) and 34(10). According to a classification scheme(11), these Koc values suggest that chloroform is expected to have very high to moderate mobility in soil.
Literature: (1) Dural NH, Peng D; Hazard Ind Wastes 27: 528-37 (1995) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 4-2 (1990) (3) Dilling WL et al; Environ Sci Technol 9: 833-8 (1975) (4) Hutzler NJ et al; Amer Chem Soc 186th Mtg Div Environ Chem Preprint 23: 499-502 (1983) (5) Roberts PV et al; Water Res 16: 1025-35 (1982) (6) Wilson JT et al; J Environ Qual 10: 501-6 (1981) (7) Borisover MD, Graber ER; Chemosphere 34: 1761-76 (1997) (8) Harrison EM, Barker JF; J Contamin Hydrol 1: 349-73 (1987) (9) Chu W, Chan K-H; Sci Total Environ 248: 1-10 (2000) (10) Washington JW, Cameron BA; Environ Toxicol Chem 20: 1909-15 (2001) (11) Swann RL et al; Res Rev 85: 17-28 (1983)

Chloromethane

METHYL CHLORIDE

74-87-3

Methane, chloro-

Monochloromethane

Methylchloride

Artic

Methylchlorid

CH3Cl

Clorometano

Chloor-methaan

Metylu chlorek

Chlor-methan

Cloruro di metile

Chlorure de methyle

RCRA waste number U045

R 40

MeCl

Refrigerant R40

CHEBI:36014

A6R43525YO

R-40

Freon 40

Caswell No. 557

Clorometano [Italian]

Chlor-methan [German]

Chlorocarbon

Methylchlorid [German]

Methyl Chloride (ca. 5.7% in Tetrahydrofuran, ca. 1mol/L)

Chloor-methaan [Dutch]

Metylu chlorek [Polish]

MFCD00000872

Cloruro di metile [Italian]

Chlorure de methyle [French]

Merrifield's peptide resin, 50-100 mesh

CCRIS 1124

HSDB 883

EINECS 200-817-4

UN1063

RCRA waste no. U045

EPA Pesticide Chemical Code 053202

carbon-chlorine

chloro-methane

methyl-chloride

UNII-A6R43525YO

AI3-01707

Chloro Methyl group

Cl-Me

a rt i c

Chloromethane 99.9%

EC 200-817-4

Chloromethane, >=99.5%

METHYL CHLORIDE [II]

METHYL CHLORIDE [MI]

2108-20-5

METHYL CHLORIDE [HSDB]

METHYL CHLORIDE [IARC]

CHEMBL117545

DTXSID0021541

METHYL CHLORIDE [MART.]

InChI=1/CH3Cl/c1-2/h1H

BBFYMZCRBPASGM-UHFFFAOYSA-N

LKYXEULZVGJVTG-UHFFFAOYSA-N

DTXSID101316851

UN 1063

Chloromethane 100 microg/mL in Methanol

Methyl chloride, or Refrigerant gas R 40

Merrifield's peptide resin, 200-400 mesh

Chloromethane on Rasta Resin, 50-100 mesh

M2813

NS00019473

C19446

Q422709

Chloromethane 1M, in tert-butyl methyl ether, anhydrous

Methyl chloride, or Refrigerant gas R 40 [UN1063] [Flammable gas]

JandaJel(TM)-Cl, 100-200 mesh, extent of labeling: 0.8-1.2 mmol/g Cl loading, 2 % cross-linked

JandaJel(TM)-Cl, 200-400 mesh, extent of labeling: 0.45-0.70 mmol/g Cl loading, 2 % cross-linked

JandaJel(TM)-Cl, 50-100 mesh, extent of labeling: 0.45-0.70 mmol/g Cl loading, 2 % cross-linked

Merrifield's peptide resin, 100-200 mesh, extent of labeling: 3.5-4.5 mmol/g Cl- loading, 1 % cross-linked

Merrifield's peptide resin, 200-400 mesh, extent of labeling: 1.0-1.5 mmol/g Cl- loading, 2 % cross-linked

Merrifield's peptide resin, 200-400 mesh, extent of labeling: 1.5-2.0 mmol/g Cl- loading, 1 % cross-linked

Merrifield's peptide resin, 200-400 mesh, extent of labeling: 2.0-2.5 mmol/g Cl- loading, 2 % cross-linked

Merrifield's peptide resin, 200-400 mesh, extent of labeling: 3.0-3.5 mmol/g Cl- loading, 1 % cross-linked

Merrifield's peptide resin, 200-400 mesh, extent of labeling: 3.5-4.5 mmol/g Cl- loading, 1 % cross-linked

Merrifield's peptide resin, 50-100 mesh, extent of labeling: 2.5-4.0 mmol/g Cl- loading, 1 % cross-linked with divinylbenzene

Merrifield's peptide resin, 70-90 mesh, extent of labeling: 1.0-1.5 mmol/g Cl- loading, 1 % cross-linked

Merrifield's peptide resin, 70-90 mesh, extent of labeling: 1.5-2.0 mmol/g Cl- loading, 1 % cross-linked

StratoSpheres(TM) PL-CMS resin, 100-200 mesh, extent of labeling: 1.0 mmol/g loading, 1 % cross-linked

StratoSpheres(TM) PL-CMS resin, 100-200 mesh, extent of labeling: 2.0 mmol/g loading, 1 % cross-linked

StratoSpheres(TM) PL-CMS resin, 200-400 mesh, extent of labeling: 1.0 mmol/g loading, 1 % cross-linked

StratoSpheres(TM) PL-CMS resin, 30-40 mesh, extent of labeling: 1.0 mmol/g loading, 1 % cross-linked

StratoSpheres(TM) PL-CMS resin, 30-40 mesh, extent of labeling: 2.0 mmol/g loading, 1 % cross-linked

StratoSpheres(TM) PL-CMS resin, 50-100 mesh, extent of labeling: 2.0 mmol/g loading, 1 % cross-linked

StratoSpheres(TM) PL-CMS resin, 50-100 mesh, extent of labeling: 4.0 mmol/g loading, 1 % cross-linked

The Henry's Law constant for methyl chloride is 8.82X10-3 atm-cu m/mole(1). This Henry's Law constant indicates that methyl chloride is expected to volatilize rapidly from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 2.1 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 2.8 days(SRC). Methyl chloride's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). Methyl chloride is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 4,300 mm Hg at 25 deg C(3).
Literature: (1) Gossett JM; Environ Sci Technol 21: 202-8 (1987) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Daubert TE, Danner RP; Physical and thermodynamic properties of pure chemicals: data compilation. Design Inst Phys Prop Data, Amer Inst Chem Eng. NY,NY: Hemisphere Pub. Corp 4 Vol (1989)
Literature: #The volatilization half-life for 1 ppm methyl chloride from a stirred beaker 6.5 cm deep is 27.6 min(1) which converts to a half-life at a 1 m depth of 7.1 hr(SRC). According to a mathematical model, the cumulative volatilization loss of methyl chloride during the first year after placement 1 m beneath the ground, assuming no water evaporation, is 66.9% and 22.3% for sandy and clay soil, respectively(2). When the buried methyl chloride is subject to 0.1 cm/day of steady upward water flow (water evaporation) the cumulative loss at the end of a year is 77.0% for sandy soil and 42.7% for clay soil(SRC).
Literature: (1) Dilling WL; Environ Sci Technol (1977) (2) Jury WA et al; Water Resources Res 26: 13-20 (1990)

Using a structure estimation method based on molecular connectivity indices(1), the Koc for methyl chloride can be estimated to be 13(SRC). According to a classification scheme(2), this estimated Koc value suggests that methyl chloride is expected to have very high mobility in soil.
Literature: (1) US EPA; Estimation Program Interface (EPI) Suite. Ver. 4.11. Nov, 2012. Available from, as of Jan 19, 2016: http://www2.epa.gov/tsca-screening-tools (2) Swann RL et al; Res Rev 85: 17-28 (1983)

IODOMETHANE

Methyl iodide

74-88-4

Monoiodomethane

Methane, iodo-

Methyljodid

Jod-methan

Methyliodide

Methyl iodine

Methyljodide

Iodometano

Joodmethaan

Metylu jodek

Iodure de methyle

CH3I

Monoioduro di metile

Halon 10001

Methyliodid

iodo-methane

RCRA waste number U138

Monoiodmethan

Iodmethan

iodo methane

NSC 9366

DAT010ZJSR

IODOMETHANE-13C-D3

CHEBI:39282

NSC-9366

MFCD00001073

MEI

Joodmethaan [Dutch]

Iodometano [Italian]

Methyljodid [German]

Methyljodide [Dutch]

Jod-methan [German]

Metylu jodek [Polish]

Iodure de methyle [French]

CCRIS 395

Monoioduro di metile [Italian]

HSDB 1336

EINECS 200-819-5

UNII-DAT010ZJSR

UN2644

RCRA waste no. U138

iodmethane

iodometane

iodomethan

iodornethane

methiodide

methyliodine

carbon-iodine

mehyl iodide

methy iodide

metyl iodide

Methyl-iodide

meth-yl iodide

1-iodomethane

ICH3

EC 200-819-5

METHYL IODIDE [MI]

METHYL IODIDE [HSDB]

METHYL IODIDE [IARC]

WLN: I1

CHEMBL115849

DTXSID0024187

Iodomethane, ampule of 100 mg

DTXSID60167860

InChI=1/CH3I/c1-2/h1H

NSC9366

BCP26570

BBL034228

Iodomethane, for synthesis, 99.0%

STL281179

AKOS009031541

Methyl iodide [UN2644] [Poison]

MCULE-1718786667

UN 2644

Iodomethane, purum, >=99.0% (GC)

Iodomethane contains copper as stabilizer

BP-11384

Iodomethane, SAJ first grade, >=93.0%

Iodomethane, SAJ special grade, >=99.5%

I0060

NS00001340

C18448

Iodomethane, puriss., redist., >=99.5% (GC)

Q421729

F2190-0170

Iodomethane, contains copper as stabilizer, ReagentPlus(R), 99%

Iodomethane, contains copper as stabilizer, ReagentPlus(R), 99.5%

Iodomethane, 2000 mug/mL in methanol: water (4:1), analytical standard

Iodomethane, 2M soln. in tert-butyl methyl ether (stabilized with Cu)

The Henry's Law constant for methyl iodide is 0.00526 atm-cu m/mole at 25 deg C(1). This Henry's Law constant indicates that methyl iodide should volatilize from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 1.3 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 4.8 days(SRC). The Henry's Law constant in seawater of salinity 30.4 g dissolved inorganic matter/kg seawater was 0.00354 atm-cu m/mole at 20 deg C(4) indicating a lower volatization rate for methyl iodide in seawater(SRC). Dissipation of methyl iodide from open surface water was found to be primarily a result of volatilization(4). Experiments conducted under indoor conditions resulted in a first-order half-life of 29 hours under static conditions and 6.5 hours when stirred at low speed with a magnetic stirrer(5). After 6 days, less that 1% of the methyl iodide was detected as iodide ion. Methyl iodide's Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). Methyl iodide is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 405 mm Hg at 25 deg C(3).
Literature: (1) Hunter-Smith RJ et al; Tellus Ser B B35: 170-6 (1983) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Boublik T et al; The Vapor Pressures of Pure Substances Amsterdam: Elsevier p. 51 (1984) (4) Moore RM et al; Chemosphere 30: 183- 91 (1995) (5) Gan J, Yates SR; J Agric Food Chem 44: 4001-8 (1996)
Literature: #Experiments were conducted to assess the volatilization loss of methyl iodide, applied at 30 cm, from 60-cm packed soil columns with different soils and under various soil surface conditions(1). In Greenfield sandy loam, the greatest cumulative loss occurred in nontarp applications, 94%, and the least in a high-barrier plastic tarp treatment, 75%. Volatilization losses with a polyethylene film was 90% and therefore this treatment was ineffective at preventing volatilization loss. Volatilization losses using a polyethylene film were significantly lower, 38% and 53%, from two soils high in organic matter and capable of rapidly degrading the chemical.
Literature: (1) Gan J et al; J Environ Qual 26: 1107-15 (1997)

Using a structure estimation method based on molecular connectivity indices(1), the Koc for methyl iodide can be estimated to be 14(SRC). According to a classification scheme(2), this estimated Koc value suggests that methyl iodide should have very high mobility in soil. The soil/water distribution coefficient of methyl iodide in various soils were (soil, Kd): Greenfield sandy loam, 0.09; Linne clay loam, 0.15; Carsetas loamy sand, 0.16; and potting mix, 0.55(3).
Literature: (1) Meylan WM et al; Environ Sci Technol 26: 1560-67 (1992) (2) Swann RL et al; Res Rev 85: 17-28 (1983) (3) Gan J, Yates SR; J Agric Food Chem 44: 4001-8 (1996) (4) Gan J et al; J Environ Qual 26: 1107-15 (1997)

Chloroethane

ETHYL CHLORIDE

Ethane, chloro-

75-00-3

Chlorene

Chelen

Monochloroethane

Anodynon

Chlorethyl

Cloretilo

Dublofix

Chloryl

Ether chloratus

Ether muriatic

Muriatic ether

Aethylis chloridum

Chloryl anesthetic

Ether hydrochloric

Hydrochloric ether

Monochlorethane

Narcotile

Kelene

Aethylis

Chloridum

Aethylchlorid

Chloorethaan

Chloroaethan

Cloroetano

Etylu chlorek

Cloruro di etile

C2H5Cl

Chlorure D'ethyle

NCI-C06224

CCRIS 3349

HSDB 533

mono-chloroethane

Chloryle anesthetic

AI3-24474

Ethyl chloride [USP]

EINECS 270-142-8

46U771ERWK

68411-72-3

CHEBI:47554

Ethyl chloride (USP)

Ether chloridum

Chloorethaan [Dutch]

Cloroetano [Italian]

Chloroaethan [German]

ethylchloride

Aethylchlorid [German]

Aethylchloride

Aethylchloride [German]

Etylu chlorek [Polish]

MFCD00000961

Chlorure d'ethyle [French]

Cloruro di etile [Italian]

Gebauer's Ethyl Chloride

EINECS 200-830-5

UN1037

chloranylethane

UNII-46U771ERWK

aetyl chloride

chloro-ethane

1-Chloroethane #

Chloroethane 99%

ETHYL CHLORIDE (CHLOROETHANE)

UN 1037

CHLOROETHYL GROUP

1-CHLORO-ETHANE

CHLOROETHANE [IARC]

EC 200-830-5

Chloroethane, >=98.0%

Chloroethane, >=99.7%

Chloroethane, >=99.8%

ETHYL CHLORIDE [MI]

CHEMBL46058

ETHYL CHLORIDE [HSDB]

ETHYL CHLORIDE [VANDF]

Ethane, chloro- (8CI,9CI)

ETHYL CHLORIDE [MART.]

DTXSID1020302

ETHYL CHLORIDE [WHO-DD]

Chloroethane, purum, >=98.0%

ETHYL CHLORIDE [USP IMPURITY]

AKOS000261558

DB13259

Chloroethane 100 microg/mL in Methanol

Chloroethane 1000 microg/mL in Methanol

InChI=1/C2H5Cl/c1-2-3/h2H2,1H

C2882

C2883

Ethyl chloride [UN1037] [Flammable gas]

F 160

NS00019447

R 160

C18248

D04088

A838306

Q409133

Chloroethane (ca. 15% in Tetrahydrofuran, ca. 2.0mol/L)

25052-55-5

The Henry's Law constant for ethyl chloride is 1.11X10-02 atm-cu m/mole(1). This Henry's Law constant indicates that ethyl chloride is expected to volatilize rapidly from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 0.9 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 3.2 days(SRC). Ethyl chloride's Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of ethyl chloride from dry soil surfaces may exist(SRC) based upon a vapor pressure of 1.01X10+03 mm Hg(3).

Using a structure estimation method based on molecular connectivity indices(1), the Koc for ethyl chloride can be estimated to be 24(SRC). According to a classification scheme(2), this estimated Koc value suggests that ethyl chloride is expected to have very high mobility in soil.

VINYL FLUORIDE

Fluoroethene

Fluoroethylene

Ethene, fluoro-

75-02-5

Monofluoroethylene

Monofluoroethene

Ethylene, fluoro-

1-Fluoroethylene

2598465ICX

Vinylfluoride

Fluoroethylene (IUPAC)

CCRIS 7213

HSDB 807

EINECS 200-832-6

UN1860

BRN 1731574

C2H3F

UNII-2598465ICX

Vinyl fluoride, inhibited

EC 200-832-6

Vinyl fluoride, Fluoroethene

4-01-00-00694 (Beilstein Handbook Reference)

UN 1860 (Salt/Mix)

VINYL FLUORIDE [HSDB]

VINYL FLUORIDE [IARC]

DTXSID3021435

CHEBI:51314

AKOS006229639

FC 1141

InChI=1/C2H3F/c1-2-3/h2H,1H

NS00006744

C19185

Q420955

Vinyl fluoride, inhibited [UN1860] [Flammable gas]

The Henry's Law constant for vinyl fluoride is estimated as 0.12 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This Henry's Law constant indicates that vinyl fluoride is expected to volatilize rapidly from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 2 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 3 days(SRC). Vinyl fluoride's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of vinyl fluoride from dry soil surfaces may exist(SRC) based upon an extrapolated vapor pressure of 1.98X10+4 mm Hg(3).

Using a structure estimation method based on molecular connectivity indices(1), the Koc for vinyl fluoride can be estimated to be 24(SRC). According to a classification scheme(2), this estimated Koc value suggests that vinyl fluoride is expected to have very high mobility in soil.

DICHLOROMETHANE

Methylene chloride

75-09-2

Methylene dichloride

Methane, dichloro-

Methylene bichloride

Methane dichloride

Solaesthin

Solmethine

Narkotil

Freon 30

Aerothene MM

Metylenu chlorek

Chlorure de methylene

Dichlormethan

Metaclen

Soleana VDA

Khladon 30

CH2Cl2

F 30 (chlorocarbon)

Methylenum chloratum

R30 (refrigerant)

RCRA waste number U080

Caswell No. 568

dichloro-methane

NCI-C50102

R 30

HCC 30

Chloride, Methylene

Bichloride, Methylene

Dichloride, Methylene

HSDB 66

CCRIS 392

dichlormethane

Methoklone

Methylenchlorid

Salesthin

NSC 406122

UN 1593

dichloro methane

Chlorodorm D

F 30

EINECS 200-838-9

UNII-588X2YUY0A

EPA Pesticide Chemical Code 042004

BRN 1730800

588X2YUY0A

DTXSID0020868

CHEBI:15767

AI3-01773

Methylene chloride [NF]

NSC-406122

Dichloromethane, HPLC Grade

DTXCID40868

EC 200-838-9

4-01-00-00035 (Beilstein Handbook Reference)

MFCD00000881

NSC406122

Methylene chloride (NF)

DICHLOROMETHANE (IARC)

DICHLOROMETHANE [IARC]

DICHLOROMETHANE (MART.)

DICHLOROMETHANE [MART.]

METHYLENE CHLORIDE (II)

METHYLENE CHLORIDE [II]

Metylenu chlorek [Polish]

METHYLENE CHLORIDE (EP MONOGRAPH)

METHYLENE CHLORIDE [EP MONOGRAPH]

Methylene chloride; Dichloromethane; DCM

MFCD00000882

Chlorure de methylene [French]

Dichloromethane (Methylene Chloride)

UN1593

DICHLOROMETHANE, NF

RCRA waste no. U080

DICHLOROMETHANE, ACS

dichioromethane

dichlormetane

dichloromeihane

dichlorometan

dichlorometane

dichloromethan

dichoromethane

dicloromethane

methylenchoride

metylenchloride

Aerothene

Driverit

Nevolin

dichlor-methane

dichlorometliane

dichlorornethane

dicliloromethane

methylenchloride

methylenechlorid

methYIenechlorid

di-chloromethane

dichloromethane-

methlyenechloride

methylenechloride

methlene chloride

methyene chloride

methylen chloride

methylene chlorie

methylene cloride

metylene chloride

Methylene choride

mehtylene chloride

methlyene chloride

methylene,chloride

methylene-chloride

dichloro -methane

dichloro- methane

methylenedichloride

Distillex DS3

Dichloromethane, ACS reagent, >=99.5%, contains 40-150 ppm amylene as stabilizer

M-clean D

methyl ene chloride

MeCl2

DCM,SP Grade

methylene di chloride

N,N-methylenechloride

dichloromethane radical

Methylene chloride ACS

Cl2CH2

H2CCl2

Dichloromethane, anhydrous

Dichloromethane, for HPLC

NCIMech_000221

WLN: G1G

Dichloromethane (DOT:OSHA)

Dichloromethane, >=99.9%

CHEMBL45967

R 30 (REFRIGERANT)

Dichloromethane, AR, >=99%

Dichloromethane (Peptide Grade)

METHYLENE CHLORIDE [MI]

METHYLENE CHLORIDE [FCC]

DTXSID20188293

DTXSID60166893

METHYLENE CHLORIDE [HSDB]

Dichloromethane, LR, >=99.5%

Dichloromethane, purification grade

dichloromethane; methylene chloride

METHYLENE CHLORIDE [VANDF]

Dichloromethane(Methylene Chloride)

Dichloromethane, analytical standard

Dichloromethane, Environmental Grade

METHYLENE CHLORIDE [USP-RS]

Tox21_202526

STL264204

AKOS009031498

InChI=1/CH2Cl2/c2-1-3/h1H

Dichloromethane [UN1593] [Poison]

Dichloromethane, ACS reagent, 99.5%

MCULE-1114735075

CAS-75-09-2

Dichloromethane, for HPLC, >=99.7%

Dichloromethane, Spectrophotometric Grade

NCGC00091504-01

NCGC00260075-01

Dichloromethane, Guaranteed Reagent Grade

SY010434

Dichloromethane 100 microg/mL in Methanol

Dichloromethane, suitable for PCB analysis

DESFLURANE IMPURITY E [EP IMPURITY]

Dichloromethane 1000 microg/mL in Methanol

D0529

D3478

M0629

NS00004151

Dichloromethane, 99%, stabilized with ethanol

Dichloromethane, for HPLC, >=99.8% (GC)

Dichloromethane, SAJ first grade, >=99.0%

Dichloromethane, Selectophore(TM), >=99.5%

C02271

D02330

Dichloromethane, analytical standard, stabilized

Dichloromethane, JIS special grade, >=99.0%

L023970

Q421748

Q425210

J-610006

Dichloromethane, 99%, stab. with ca. 50ppm amylene

Methylene Chloride HPLC grade Stabilized with Amylene

Dichloromethane, glass distilled HRGC/HPLC trace grade

Dichloromethane, TLC high-purity grade, >=99.8% (GC)

Dichloromethane HPLC, UV/IR, min. 99.8%, isocratic grade

Dichloromethane, special, 99.9%, contains 40-60 ppm Amylene

Dichloromethane, for HPLC, >=99.8%, contains amylene as stabilizer

Dichloromethane, Selectophore(TM), >=99.5% (GC), inhibitor-free

Dichloromethane, technical grade, 95%, contains 40-60 ppm Amylene

Methylene chloride, European Pharmacopoeia (EP) Reference Standard

Dichloromethane, puriss. p.a., ACS reagent, reag. ISO, >=99.9% (GC)

Dichloromethane, UV HPLC spectroscopic, 99.9%, contains 40-60 ppm Amylene

Dichloromethane, ACS reagent, >=99.5%, contains 50 ppm amylene as stabilizer

Dichloromethane, anhydrous, >=99.8%, contains 40-150 ppm amylene as stabilizer

Dichloromethane, anhydrous, contains 40-150 ppm amylene as stabilizer, ZerO2(TM), >=99.8%

Dichloromethane, biotech. grade, 99.9%, contains 40-150 ppm amylene as stabilizer

Dichloromethane, contains 40-150 ppm amylene as stabilizer, ACS reagent, >=99.5%

Dichloromethane, for HPLC, >=99.9%, contains 40-150 ppm amylene as stabilizer

Dichloromethane, puriss., meets analytical specification of Ph.??Eur., NF, >=99% (GC)

Methylene Chloride, Pharmaceutical Secondary Standard; Certified Reference Material

Dichloromethane, >=99.9%, capillary GC grade, suitable for environmental analysis, contains amylene as stabilizer

Dichloromethane, ACS spectrophotometric grade, >=99.5%, contains 50-150 ppm amylene as stabilizer

Dichloromethane, Laboratory Reagent, >=99.9% (without stabilizer, GC), contains 0.1-0.4% ethanol as stabilizer

Dichloromethane, p.a., ACS reagent, reag. ISO, reag. Ph. Eur., 99.8%, contains 40-60 ppm Amylene

Dichloromethane, puriss. p.a., ACS reagent, reag. ISO, dried, >=99.8% (GC), <=0.001% water

M.C

Residual Solvent Class 2 - Methylene chloride, United States Pharmacopeia (USP) Reference Standard

The Henry's Law constant for dichloromethane is 3.25X10-3 atm-cu m/mole(1). This Henry's Law constant indicates that dichloromethane is expected to volatilize rapidly from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 2.9 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 3.7 days(SRC). Half-lives for the evaporation from water of 3-5.6 hours have been determined at moderate mixing conditions(4). When released into an estuarine bay, all the chemical dissipated within 4 km of the release point in the spring and within 8 km in the winter under ice(5). Dichloromethane's Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). Dichloromethane is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 435 mm Hg at 25 °C(3).

Dichloromethane has reported experimentally derived Koc values of 28(1), 36(2), 48 and 8(3). According to a classification scheme(4), these Koc values suggest that dichloromethane is expected to have very high mobility in soil. Dichloromethane is adsorbed strongly to peat moss, less strongly to clay, only slightly to dolomite limestone, and not at all to sand(5).

DIIODOMETHANE

75-11-6

Methylene iodide

Methane, diiodo-

Methylene diiodide

MI-Gee

Dijodmethan

Methylenjodid

diiodo-methane

CH2I2

di-iodomethane

NSC 35804

Methylene iodide-13C,d2

NSC-35804

3J731705OX

Dijodmethan [Czech]

Methylenjodid [Czech]

EINECS 200-841-5

methvleneiodide

methyleneiodide

methyleniodid

Methyl diiodide

CCRIS 8551

Mi-gee brand

UNII-3J731705OX

bis(iodanyl)methane

SCHEMBL185

WLN: I1I

METHYLENE IODIDE [MI]

DTXSID4058784

AMY25773

NSC35804

STR03006

BBL011419

MFCD00001079

STL146526

AKOS002664705

MCULE-8023612181

BP-21047

Diiodomethane, SAJ first grade, >=98.0%

D0610

NS00022756

diiodomethane; di-iodomethane; methylene iodide

A838327

Q425692

F0001-1891

Diiodomethane, ReagentPlus(R), 99%, contains copper as stabilizer

IODOFORM

Triiodomethane

75-47-8

Methane, triiodo-

Carbon triiodide

Jodoform

Trijodmethane

CHI3

Dezinfekt V

Iodoformum

NCI-C04568

CCRIS 346

methyl triiodide

HSDB 4099

EINECS 200-874-5

NSC 26251

NSC-26251

UNII-KXI2J76489

DTXSID4020743

CHEBI:37758

AI3-52396

KXI2J76489

DTXCID40743

MFCD00001069

NCGC00091389-01

IODOFORM (MART.)

IODOFORM [MART.]

Jodoform [Czech]

Iodoform [JAN]

IODOFORM (USP MONOGRAPH)

IODOFORM [USP MONOGRAPH]

Trijodmethane [Czech]

tri-iodomethane

CAS-75-47-8

Iodoform [USP:JAN]

Carbontriiodide

Iodoform (TN)

tris(iodanyl)methane

Iodoform, 99%

TRIIODO METHANE

IODOFORM [HSDB]

IODOFORM [INCI]

IODOFORM [MI]

WLN: IYII

IODOFORMUM [HPUS]

Iodoform (JP17/USP)

IODOFORM [WHO-DD]

Iodoform, SAJ first grade

CHEMBL1451116

NSC26251

Tox21_111124

Tox21_202389

Tox21_302774

AKOS009031506

Iodoform, purum, >=99.0% (AT)

DB13813

MCULE-5976787287

Iodoform, puriss., 99.0-100.5%

s12111

NCGC00091389-02

NCGC00091389-03

NCGC00256394-01

NCGC00259938-01

AS-14199

NS00006693

D01910

A838427

Q412393

J-650249

The Henry's Law constant for iodoform is estimated as 3.1 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This Henry's Law constant indicates that iodoform is expected to volatilize from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 40 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 25 days(SRC). Iodoform's Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). Iodoform is not expected to volatilize from dry soil surfaces(SRC) based upon an estimated vapor pressure of 0.040 mm Hg(SRC), determined from a fragment constant method(3).
Literature: (1) Meylan WM, Howard PH; Environ Toxicol Chem 10: 1283-93 (1991) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Lyman WJ; p 31 in Environmental Exposure From Chemicals Vol I, Neely WB, Blau GE(eds), Boca Raton, FL: CRC Press (1985)

Using a structure estimation method based on molecular connectivity indices(1), the Koc for iodoform can be estimated to be 35(SRC). According to a classification scheme(2), this estimated Koc value suggests that iodoform is expected to have very high mobility in soil.
Literature: (1) Meylan WM et al; Environ Sci Technol 26: 1560-67 (1992) (2) Swann RL et al; Res Rev 85: 17-28 (1983)

1-Bromo-2-methylpropane

78-77-3

ISOBUTYL BROMIDE

iso-Butyl bromide

Propane, 1-bromo-2-methyl-

1-Bromo-2-methyl-propane

i-Butyl bromide

Bromoacetaldehydedimethylacetal

5OEC0BW987

DTXSID1052539

NSC-8416

MFCD00000217

Bromoisobutane

CCRIS 349

2-methylpropyl bromide

NSC 8416

EINECS 201-141-2

isobutylbromid

isobutylbromide

UNII-5OEC0BW987

i-butylbromide

iso-butylbromide

isobutyl-bromide

AI3-18130

i-BuBr

2-methylbromopropane

2-methylpropylbromide

iso-C4H9Br

2-methyl bromopropane

1-bromo-2methylpropane

1-bromo-2-methylpropan

l-bromo-2-methylpropane

3-bromo-2-methylpropane

1 -bromo-2-methylpropane

1-bromo 2-methyl propane

1-bromo-2-methyl propane

EC 201-141-2

SCHEMBL7399

ISOBUTYL BROMIDE [MI]

2-Bromo-1,1-Dimethyl Ethane

CHEMBL346532

DTXCID2031112

1-Bromo-2-methylpropane, 99%

WLN: E1Y1&1

NSC8416

AMY25783

BCP21482

Tox21_303878

BBL036259

STL264117

AKOS000118762

MCULE-6039420480

PB48146

UN 2342

CAS-78-77-3

NCGC00357138-01

VS-13394

A9430

B0616

NS00006245

EN300-19287

P19652

J-504405

Q15632844

F1908-0100

InChI=1/C4H9Br/c1-4(2)3-5/h4H,3H2,1-2H

1,1,2,2-TETRACHLOROETHANE

79-34-5

s-Tetrachloroethane

Acetylene tetrachloride

Ethane, 1,1,2,2-tetrachloro-

sym-Tetrachloroethane

Bonoform

Cellon

Tetrachlorethane

Westron

1,1,2,2-Tetrachlorethane

1,1,2,2-Tetrachloraethan

1,1-Dichloro-2,2-dichloroethane

Tetrachlorure d'acetylene

RCRA waste number U209

NCI-C03554

Dichloro-2,2-dichloroethane

Tetrachloroethane [ISO]

Tetrachloroethane, 1,1,2,2-

1,1,2,2-Tetracloroetano

1,1,2,2-Czterochloroetan

NSC 60912

1,1,2,2-Tetrachloorethaan

1,1,2,2-Tetrachloro-Ethane

1L6BI049XV

DTXSID7021318

CHEBI:36026

NSC-60912

TCE (ambiguous)

Caswell No. 826

Acetosol

Tetrachloroethane (VAN)

CCRIS 578

HSDB 123

Tetrachlorure d'acetylene [French]

EINECS 201-197-8

1,1,2,2-Czterochloroetan [Polish]

1,1,2,2-Tetrachloorethaan [Dutch]

1,1,2,2-Tetrachloraethan [German]

1,1,2,2-Tetrachlorethane [French]

1,1,2,2-Tetracloroetano [Italian]

RCRA waste no. U209

EPA Pesticide Chemical Code 078601

BRN 0969206

UNII-1L6BI049XV

AI3-04597

sym-tetrachlorethane

CHCl2CHCl2

WLN: GYGYGG

R 130 (refrigerant)

1,2,2-Tetracloroetano

1,2,2-Czterochloroetan

1,2,2-Tetrachloraethan

1,2,2-Tetrachlorethane

1,2,2-Tetrachloorethaan

1,2,2-Tetrachloroethane

SCHEMBL2564

(CHCl2)2

Ethane,1,2,2-tetrachloro-

4-01-00-00144 (Beilstein Handbook Reference)

CHEMBL47258

TETRACHLOROETHANE [MI]

1,1,2,2,-tetrachloroethane

1,1,2,2-tetra chloroethane

DTXCID201318

TETRACHLOROETHANE [HSDB]

NSC60912

1,1,2,2-tetrakis(chloranyl)ethane

Tox21_200074

MFCD00000848

AKOS009029114

ETHANE,1,1,2,2-TETRACHLORO

MCULE-4029260741

UN 1702

1,1,2,2-TCE

CAS-79-34-5

NCGC00091543-01

NCGC00091543-02

NCGC00257628-01

1,1,2,2-TETRACHLOROETHANE [IARC]

NS00010827

S0654

T0063

EN300-19275

C19534

1,1,2,2-Tetrachloroethane, analytical standard

1,1,2,2-Tetrachloroethane, reagent grade, 97%

A839654

Q161275

InChI=1/C2H2Cl4/c3-1(4)2(5)6/h1-2

J-503708

1 pound not1 pound not2 pound not2-tetrachloroethane

1,1,2,2-Tetrachloroethane, reagent grade, >=98.0%

1,1,2,2-Tetrachloroethane 100 microg/mL in Methanol

F0001-2074

1,1,2,2-Tetrachloroethane, JIS special grade, >=97.0%

1,5-Dichloroanthraquinone

82-46-2

1,5-dichloroanthracene-9,10-dione

9,10-Anthracenedione, 1,5-dichloro-

1,5-Dichloro-9,10-anthraquinone

1,5-Dichloranthrachinon

ANTHRAQUINONE, 1,5-DICHLORO-

1, 5-Dichloroanthraquinone

S335V6MF9E

1,5-Dichloroanthra-9,10-quinone

1,5-dichloro-9,10-anthracenedione

NSC-13969

1,5-Dichloranthrachinon [Czech]

EINECS 201-424-0

NSC 13969

UNII-S335V6MF9E

AI3-38301

1,5-Dichloro-9,10-anthracenedione; 1,5-Dichloro-9,10-anthraquinone; 1,5-Dichloroanthraquinone; NSC 13969

NSC13969

9, 1,5-dichloro-

1,5-Dichloroantraquinone

Maybridge1_002222

Anthraquinone,5-dichloro-

CBMicro_015239

1,5-bischloroanthraquinone

1,5-dichloro anthraquinone

1,5-dichloro-anthraquinone

SCHEMBL125609

DTXSID3058874

HMS547M22

1,5-Dichloroanthraquinone, 96%

CCG-41659

MFCD00001190

STK054157

WLN: L C666 BV IVJ DG KG

1,5-Dichloroanthra-9,10-quinone #

AKOS001583243

CS-W012310

AC-11726

AS-14370

BIM-0015275.P001

D0328

EU-0066588

NS00038203

1,5-dichloro-9,10-dihydroanthracene-9,10-dione

SR-01000631719-1

W-104174

Q27288514

InChI=1/C14H6Cl2O2/c15-9-5-1-3-7-11(9)14(18)8-4-2-6-10(16)12(8)13(7)17/h1-6

2,4,6-TRICHLOROANISOLE

87-40-1

1,3,5-Trichloro-2-methoxybenzene

Tyrene

2,4,6-Trichloro-1-methoxybenzene

TRICHLOROANISOLE

Benzene, 1,3,5-trichloro-2-methoxy-

Methyl 2,4,6-trichlorophenyl ether

Anisole, 2,4,6-trichloro-

2,4.6-Trichloroanisole

1,3,5-trichloro-2-methoxy-benzene

MFCD00000588

NSC-35142

31O3X41254

UNII-31O3X41254

EINECS 201-743-5

NSC 35142

2,6-Trichloroanisole

AI3-09173

Anisole,4,6-trichloro-

2,4,6-Trichloro-Anisole

SCHEMBL54507

1,5-Trichloro-2-methoxybenzene

DTXSID9073886

CHEBI:19333

2,4,6-Trichloroanisole, 99%

Methyl 2,6-trichlorophenyl ether

Benzene,3,5-trichloro-2-methoxy-

NSC35142

AKOS015849927

Anisole, 2,4,6-trichloro- (8CI)

2,4,6-TRICHLOROANISOLE [MI]

1,3,5-Trichloro-2-methoxybenzene, 9CI

AS-60959

SY051443

1-METHOXY-2,4,6-TRICHLOROBENZENE

DB-057000

CS-0150571

NS00008077

T0867

Benzene, 1,3,5-trichloro-2-methoxy- (9CI)

F20912

Q209191

2,4,6-Trichloroanisole 10 microg/mL in Isooctane

2,4,6-Trichloroanisole 100 microg/mL in Methanol

2,4,6-Trichloroanisole 1000 microg/mL in Methanol

2,4,6-Trichloroanisole, PESTANAL(R), analytical standard

InChI=1/C7H5Cl3O/c1-11-7-5(9)2-4(8)3-6(7)10/h2-3H,1H

2,4,5-TRICHLORONITROBENZENE

89-69-0

1,2,4-Trichloro-5-nitrobenzene

Benzene, 1,2,4-trichloro-5-nitro-

1-Nitro-2,4,5-trichlorobenzene

5-Nitro-1,2,4-trichlorobenzene

3,4,6-Trichloronitrobenzene

2,4,5-trichloro-1-nitrobenzene

0YFY8PZD2M

DTXSID5026203

1,4,5-Trichloro-2-nitrobenzene

NSC-50660

NSC-56980

NSC-60975

2,5-Trichloronitrobenzene

WLN: WNR BG DG EG

1,4-Trichloro-5-nitrobenzene

Benzene,2,4-trichloro-5-nitro-

EINECS 201-931-7

NSC 50660

BRN 1959066

NSC60975

UNII-0YFY8PZD2M

MLS002152857

2,4,5-trichloronitro-benzene

DTXCID206203

SCHEMBL1626066

CHEMBL1323107

HMS3039M11

NSC50660

NSC56980

Tox21_200937

MFCD00007072

AKOS005149655

CAS-89-69-0

TRICHLORONITROBENZENE, 2,4,5-

1,2,4-tris(chloranyl)-5-nitro-benzene

NCGC00090855-01

NCGC00090855-02

NCGC00258491-01

AC-23991

PS-10355

SMR001224481

CS-0204672

NS00039338

T0387

1,2,4-Trichloro-5-nitrobenzene, AldrichCPR

E78965

EN300-100818

A843281

W-100364

Q27237347

InChI=1/C6H2Cl3NO2/c7-3-1-5(9)6(10(11)12)2-4(3)8/h1-2

2,4,5-Trichloronitrobenzene;1,2,4-Trichloro-5-nitrobenzene;5-Nitro-1,2,4-trichlorobenzene

4-Chlorobenzotrifluoride

98-56-6

p-Chlorobenzotrifluoride

1-CHLORO-4-(TRIFLUOROMETHYL)BENZENE

Benzene, 1-chloro-4-(trifluoromethyl)-

para-Chlorobenzotrifluoride

(p-Chlorophenyl)trifluoromethane

p-Chlorotrifluoromethylbenzene

1-(Trifluoromethyl)-4-chlorobenzene

p-Trifluoromethylphenyl chloride

4-Chloro-alpha,alpha,alpha-trifluorotoluene

p-(Trifluoromethyl)chlorobenzene

p-Chloro-a,a,a-trifluorotoluene

p-Chloro-alpha,alpha,alpha-trifluorotoluene

PARACHLOROBENZOTRIFLUORIDE

4-chloro-benzotrifluoride

NSC 10309

MFCD00000627

1219804-33-7

PCBTF

P-(TRIFLUOROMETHYL) CHLOROBENZENE

694YO34JHC

DTXSID7024821

NSC-10309

4-CHLORO-A,A,A-TRIFLUOROTOLUENE-D4

4-Chloro-.alpha.,.alpha.,.alpha.-trifluorotoluene

DTXCID004821

Toluene, p-chloro-.alpha.,.alpha.,.alpha.-trifluoro-

4-Chloro-a,a,a-trifluorotoluene

CAS-98-56-6

4-trifluoromethylchlorobenzene

CCRIS 720

para-Chlorotrifluoromethylbenzene

HSDB 4251

EINECS 202-681-1

BRN 0510203

UNII-694YO34JHC

alpha,alpha,alpha-Trifluoro-4-chlorotoluene

(4-chlorophenyl)trifluoromethane

para-Chloro-alpha,alpha,alpha-trifluorotoluene

Toluene, p-chloro-alpha,alpha,alpha-trifluoro-

4-(TRIFLUOROMETHYL)CHLOROBENZENE

4-Chlorobenzotrifuoride

4-chlorobenzo-trifluoride

EC 202-681-1

SCHEMBL196588

4-chloro trifluoromethylbenzene

4-trifluoromethyl chlorobenzene

4-Chlorobenzotrifluoride, 98%

CHEMBL1797001

1-chloro-4-trifluoromethylbenzene

1-trifluoromethyl-4-chlorobenzene

chloro-4-(trifluoromethyl)benzene

CHLOROBENZOTRIFLUORIDE, P-

BCP24446

NSC10309

Tox21_201445

Tox21_303261

P-CHLOROBENZOTRIFLUORIDE [MI]

STL268887

AKOS005067495

AM87507

NCGC00091724-01

NCGC00091724-02

NCGC00091724-03

NCGC00257114-01

NCGC00258996-01

AC-10097

4-Chloro-.alpha.,.alpha.-trifluorotoluene

p-Chloro-.alpha.,.alpha.-trifluorotoluene

NS00002149

EN300-20053

G77196

p-Chloro-.alpha.,.alpha.,.alpha.-trifluorotoluene

Q410670

1-CHLORO-4-(TRIFLUOROMETHYL)BENZENE [HSDB]

W-100075

CHLORO-ALPHA,ALPHA,ALPHA-TRIFLUOROTOLUENE, 4-

(p-Chlorophenyl)trifluoromethane;4-Chlorobenzyltrifluoride;

N-(2,4-dimethylphenyl)-3-hydroxy-naphthalene-2-carboxamide

InChI=1/C7H4ClF3/c8-6-3-1-5(2-4-6)7(9,10)11/h1-4

1-Chloro-4-(trifluoromethyl)benzene, 4-Chloro-alpha,alpha,alpha-trifluorotoluene

1-chloro-4-(trifluoromethyl)benzene; 4-Chloro-alpha,alpha,alpha-trifluorotoluene; (p-Chlorophenyl)trifluoromethane; p-Chlorotrifluoromethylbenzene; p-(Trifluoro

The Henry's Law constant for 1-chloro-4-(trifluoromethyl)benzene is estimated as 3.5X10-2 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This Henry's Law constant indicates that 1-chloro-4-(trifluoromethyl)benzene is expected to volatilize rapidly from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 4 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 5 days(SRC). 1-Chloro-4-(trifluoromethyl)benzene's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). 1-Chloro-4-(trifluoromethyl)benzene is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 7.63 mm Hg(3).
Literature: (1) Meylan WM, Howard PH; Environ Toxicol Chem 10: 1283-93 (1991) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Chemicals Vol. 3 New York, NY: Hemisphere Pub Corp (1989)

Using a structure estimation method based on molecular connectivity indices(1), the Koc of 1-chloro-4-(trifluoromethyl)benzene can be estimated to be 1600(SRC). According to a classification scheme(2), this estimated Koc value suggests that 1-chloro-4-(trifluoromethyl)benzene is expected to have low mobility in soil.
Literature: (1) US EPA; Estimation Program Interface (EPI) Suite. Ver. 4.0. Jan, 2009. Available from, as of Sept 20, 2010: http://www.epa.gov/oppt/exposure/pubs/episuitedl.htm (2) Swann RL et al; Res Rev 85: 17-28 (1983)

1-CHLORO-3-METHYLBUTANE

Isoamyl chloride

107-84-6

Butane, 1-chloro-3-methyl-

3-Methylbutyl chloride

Isopentyl chloride

4-Chloro-2-methylbutane

1-Chloro-3,3-dimethylpropane

87D3ZL9F7A

NSC-6528

MFCD00013693

isoamylchlorid

UNII-87D3ZL9F7A

NSC 6528

EINECS 203-525-5

Butane,1-chloro-3-methyl-

ISOAMYL CHLORIDE [MI]

SCHEMBL352000

SCHEMBL9258038

DTXSID2059354

NSC6528

STL280307

AKOS000262238

MCULE-9017922949

DB-040789

NS00023480

EN300-19877

D89213

Q27269816

InChI=1/C5H11Cl/c1-5(2)3-4-6/h5H,3-4H2,1-2H

CHLOROBENZENE

108-90-7

Monochlorobenzene

Phenyl chloride

Benzene chloride

Chlorbenzene

Chlorobenzol

Benzene, chloro-

Monochlorbenzene

Chlorobenzen

Monochlorbenzol

Chlorbenzol

Tetrosin SP

Clorobenzene

Chloorbenzeen

Monoclorobenzene

Monochloorbenzeen

Chlorobenzenu

chloro-benzene

Chlorobenzene, mono-

PhCl

NCI-C54886

chloro benzene

4-chlorobenzene

CP 27

NSC 8433

Abluton T30

IP Carrier T 40

NSC-8433

EINECS 270-127-6

68411-45-0

MCB

DTXSID4020298

CHEBI:28097

Benzene-13C6, chloro- (9CI)

K18102WN1G

MFCD00000530

Chloorbenzeen [Dutch]

Chlorobenzen [Polish]

Chlorobenzenu [Czech]

Caswell No. 183A

Chlorobenzene, analytical standard

Clorobenzene [Italian]

I P Carrier T 40

Monochlorbenzol [German]

Monochloorbenzeen [Dutch]

Monoclorobenzene [Italian]

HSDB 55

CCRIS 1357

C6H5Cl

EINECS 203-628-5

UN1134

RCRA waste no. U037

EPA Pesticide Chemical Code 056504

chlorobezene

chorobenzene

chlor-benzene

chloranylbenzene

p-chlorobenzene

UNII-K18102WN1G

1-chlorobenzene

3-chlorobenzene

AI3-07776

p-chlorobenzene-

mono-chlorobenzene

Chlorobenzol(DOT)

Ph-Cl

Chloorbenzeen(DUTCH)

Chlorobenzen(POLISH)

Clorobenzene(ITALIAN)

Chlorobenzene ACS grade

Chlorobenzene(ITALIAN)

Monochlorbenzol(GERMAN)

Monochloorbenzeen(DUTCH)

WLN: GR

CHLOROBENZENE [MI]

Monoclorobenzene(ITALIAN)

bmse001030

EC 203-628-5

SCHEMBL2044

CHLOROBENZENE [HSDB]

BIDD:ER0289

CHEMBL16200

DTXCID40298

Chlorobenzene, LR, >=99%

CHLOROBENZENE [USP-RS]

Chlorobenzene (ACD/Name 4.0)

Chlorobenzene, p.a., 99.5%

Chlorobenzene, AR, >=99.5%

NSC8433

Chlorobenzene, anhydrous, 99.8%

AMY40791

Chlorobenzene, for HPLC, 99.9%

Tox21_201223

STL282731

Chlorobenzene, ReagentPlus(R), 99%

AKOS000120122

MCULE-2469021740

UN 1134

Chlorobenzene 10 microg/mL in Isooctane

Chlorobenzene 100 microg/mL in Methanol

Chlorobenzene, ACS reagent, >=99.5%

NCGC00091678-01

NCGC00091678-02

NCGC00258775-01

CAS-108-90-7

PS-11980

Chlorobenzene, SAJ first grade, >=99.0%

C1948

NS00010206

S0645

Chlorobenzene [UN1134] [Flammable liquid]

Chlorobenzene, SAJ special grade, >=99.5%

EN300-18065

C06990

Chlorobenzene, anhydrous, ZerO2(TM), 99.8%

Chlorobenzene, UV HPLC spectroscopic, 99.5%

A801940

Q407768

J-002203

J-520025

F0001-0183

InChI=1/C6H5Cl/c7-6-4-2-1-3-5-6/h1-5

Chlorobenzene, puriss. p.a., ACS reagent, >=99.5% (GC)

Chlorobenzene, Pharmaceutical Secondary Standard; Certified Reference Material

Chlorobenzene, puriss., absolute, over molecular sieve (H2O <=0.005%), >=99.5% (GC)

The measured Henry's Law constant for chlorobenzene is 3.11X10-3 atm-cu m/mole at 25 deg C(1). This Henry's Law constant indicates that chlorobenzene is expected to volatilize rapidly from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 3.4 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 4.3 days(SRC). Chlorobenzene's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). Chlorobenzene is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 12 mm Hg(3). Chlorobenzene applied to soil at a uniform concentration of 1 kg/ha at depths of 1 cm and 10 cm underwent 86.5 and 23.4% loss, respectively, in a day; volatilization half-lives of 0.3 and 12.6 days, respectively, were estimated from this data(4). Volatilization half-lives of 13, 21, and 4.6 days were estimated for chlorobenzene using data obtained from an experimental marine mesocosm under simulated winter, spring, and summer conditions, respectively(5). Chlorobenzene was removed within 8 days in sterile pond water incubated in bottles open to the atmosphere(6). Volatilization rates of chlorobenzene from the wastewater-dependent constructed Tres Rios Demonstration Wetlands near Phoenix, AZ ranged from 5.11X10-6 to 8.48X10-6 sec-1, corresponding to a half-life of approximately 9 hours(7). In a closed aerated laboratory system simulating arable soil exposed to 14-C radio-labeled chlorobenzene, analysis of trapped 14-CO2 and 14-C chlorobenzene gas indicated that volatilization was the main loss mechanism with mineralization having minor importance(8).
Literature: (1) Shiu WY, Mackay D; J Chem Eng Data 42: 27-30 (1997) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Chemicals: Data Compilation. Design Inst Phys Prop Data, Amer Inst Chem Eng., New York, NY: Hemisphere Pub Corp, Vol 3 (1987) (4) Jury WA et al; J Environ Qual 13: 572-9 (1984) (5) Wakeham SG et al; Environ Sci Technol 17: 611-7 (1983) (6) Bouwer EJ; J Environ Eng 115: 741-55 (1989) (7) Keefe SH et al; Environ Sci Technol 38: 2209-26 (2004) (8) Brahushi F et al; Fresenius Environmental Bulletin 11(9a): 599-604 (2002)

Koc values of 313.1 and 146.5 were measured on Captina silt loam (1.49% organic carbon) and McLaurin sandy loam, (0.66% organic carbon), respectively(1). Equilibrium sorption constant (Ks) values of 0.295 and 0.09 were determined in Eustis fine sand (13 g/kg clay, 32 g/kg silt, 955 g/kg sand, 3.9 g/kg organic carbon) and Tampa (6 g/kg clay, 23 g/kg silt, 971 g/kg sand, and 1.3 g/kg organic carbon) soils, respectively(2); corresponding Koc values are 76 and 69(SRC). Equilibrium sorption coefficients of 0.014 and 10.20 were measured on Borden (98% sand, 1% silt, 1% clay, 0.29% organic carbon) and Mt. Lemmon (60.3% sand, 24.0% silt, 15.7% clay, 12.6% organic carbon) soils, respectively(3); corresponding Koc values are 4.8 and 81(SRC). According to a classification scheme(4), these Koc values suggest that chlorobenzene is expected to have moderate to very high mobility in soil(SRC). The sorption isotherm for chlorobenzene onto muck soil (49.0% organic carbon) was linear(5). A Kd value of 166.34 was measured for chlorobenzene using dewatered activated sludge (18% solids) that had been dried and sieved; 3.28% of the chlorobenzene was desorbed during the desorption phase of the experiment(6). Partition coefficients of 0.35, 0.33, and 0.38 were measured for chlorobenzene on primary sludge, mixed liquor solids, and digested sludge, respectively(7). Sorption coefficients of 0.48 and 0.29 were measured on primary sludge and anaerobically digested sludge, respectively(8). Partition coefficients of 48 and 29 were measured in high organic carbon (14.5%) and low organic carbon (3.6%) Sherman Island sediments, respectively(9).
Literature: (1) Walton BT et al; J Environ Qual 21: 552-8 (1992) (2) Brusseau ML; Environ Toxicol Chem 12: 1835-46 (1993) (3) Hu Q et al; Environ Toxicol Chem 14: 1133-40 (1995) (4) Swann RL et al; Res Rev 85: 23 (1983) (5) Sheng G et al; Environ Sci Technol 30: 1553-7 (1996) (6) Selvakumar A, Hsieh HN; Int J Environ Stud 30: 313-9 (1987) (7) Dobbs RA et al; Int Conf Innovative Biol Treat Toxic Wastewaters; Scholze, RJ Jr, eds; pp 585-601 (1987) (8) Dobbs RA et al; Environ Sci Technol 23: 1092-7 (1989) (9) Knezovich JP, Harrison FL; Ecotoxicol Environ Safety 15: 226-41 (1988)